棉秆生物炭对Cd2+的吸附固定作用

Adsorption and immobilization of Cd2+ by cotton straw biochar

  • 摘要: 【目的】 探究棉秆生物炭对重金属Cd2+的吸附和固定作用潜力。 【方法】 以新疆典型的农业废弃物棉花秸秆为原料,分别在500、600和700℃热解温度下制备棉秆炭(BC500、BC600和BC700),进行吸附和钝化试验。 【结果】 Cd2+初始浓度为100 mg/L时,BC500、BC600和BC700对Cd2+的吸附量分别达到10.47、9.72和11.96 mg/g。不同热解温度棉秆生物炭对Cd2+的动力吸附过程符合准二级动力吸附模型。不同热解温度棉秆生物炭中吸附的Cd2+主要以碳酸盐结合态存在,比例达到77.74%~82.09%;其次是可交换态和不可利用态,比例分别为12.14%~14.95%和5.62%~6.75%。与对照相比,添加不同热解温度棉秆生物炭使得土壤中Cd2+的水溶态和可交换态组分比例分别平均降低24.29%和6.52%;碳酸盐结合态和不可利用态组分比例分别平均增加22.49%和8.32%。 【结论】 棉秆生物炭对Cd2+具有较强的吸附潜力,施用于土壤中可有效降低土壤中Cd2+的生物可利用性。

     

    Abstract: 【Objective】 The objective of the study is to investigate the potential of cotton straw biochar for the adsorption and immobilization of heavy metals Cd2+. 【Methods】 Cotton straw biochar (BC500, BC600 and BC700) was prepared from cotton straw, a typical agricultural waste in Xinjiang, at pyrolysis temperatures of 500℃(BC500), 600℃(BC600) and 700℃(BC700), respectively. Meanwhile, experiments of adsorption and passivation were carried out. 【Results】 The results showed that at an initial concentration of 100 mg/L Cd2+, the adsorption of Cd2+ by BC500, BC600 and BC700 reached 10.47 mg/g, 9.72mg/g and 11.96mg/g, respectively. The pseudo-second order kinetic was the most suitable model for describing the adsorption of Cd2+ onto cotton straw biochar. Sequential extraction test results showed that Cd2+ was predominantly adsorbed on cotton straw biochar as carbonate-bound fraction (77.74%-82.09%). The exchangeable fraction and unavailable fraction for cotton straw biochar was low (12.14%-14.95% and 5.62%-6.75%, respectively) and the water soluble fraction was negligible (0.15%-0.55%). Compared with the control, applications of cotton straw biochar at different pyrolysis temperatures resulted in an average decrease of 24.29% and 6.52% in the water-soluble and exchangeable fraction of Cd2+, respectively, and an average increase of 22.49% and 8.32% in the carbonate-bound and unavailable fractions, respectively. 【Conclusion】 Cotton straw biochar has strong sorption potentials for Cd2+ and can be applied to soil remediation to effectively reduce the bioavailability of Cd2+.

     

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